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Transcript of Paper eec2013_submission_45 (1) (3)
Month 20xx, Volume x, No. x
International Journal of Chemical and Environmental Engineering
Study of Harvesting Rainwater System for Multimedia University (MMU) S. A. Alkaff*; M. I. Fadhel; Abdulaziz Mohamed Abdi
Faculty of Engineering and Technology, Multimedia University,
Jalan Ayer Keroh Lama, 75450, Melaka, Malaysia
Corresponding Author
E-mail: [email protected]
Tel: +6062523240
Fax: +6062316552
Abstract
Malaysia receives rainfall throughout the year with no definite significant dry period. The average rainfall of Malaysia is
greater than 2000 mm, which is more than enough for developing a feasible system. The country is therefore rich in
water resources when compared to the other regions of the world. In this paper the assessment of the rainwater
harvesting within the Multimedia University Campus, Malacca has been studied. A thorough effort was devoted to
estimate the potential of rooftop rainwater harvesting, from the different buildings within the campus. Assessment of the
rainfall profile in Malacca indicates that, the likely dry days may found through the different months in the years.
Moreover, the increase in temperature within those particular days was found noticeable, which in turn affect the
evaporation rate from the ground. Thus, more necessity for irrigating the plantation is required. The football field within
the campus was selected as a case study. A harvesting model was established to simulate the viability of the system.
Results indicate that a 5 m3 tank size achieve an average of 80% reliability to best serve the purpose of irrigation of the
football field.
Keywords: Rainwater; Harvesting; Irrigation; Dry days.
1. Introduction Rainwater harvesting is the collection of rainwater by the
use of a catchment (e.g. roof) which in turn is directed by
a system, comprising of gutters, pipes and filtration,
which eventually lead to a storage container for
consumption. The rainwater that is collected can be used
for a variety of applications which could include toilet
flushing, washing clothes and gardening. When treated
properly, it can be used for drinking as well. The concept
of harvesting rainwater in the event of scarcity is not
entirely a new idea. Ancient civilizations of ancient Egypt
and Jordan have used rainwater harvesting for crop
cultivation among other uses [1-2]. In Japan, the
government decided to subsidize its citizens to help and
encourage the transition to a greener alternative [3],
whereas Singapore are already self sufficient with 60% of
their total water consumption coming from rainfall and
treatment facilities alone. By 2061, Singapore will reach
the deadline of their water agreement with Malaysia and
are well on course in being self-reliant until then in terms
of water supply [4]. In New South Wales – Australia, the
government subsidizes the ownership of all rainwater
tanks purchased after the year 2007. The subsidization is
based on the sizes of the tanks that are purchased and any
household owner is able to apply for them [5]. With
precipitations of 330 mm annually within the Gansu
province - China, old harvesting systems became obsolete
with the rise in population and new research began in the
1980s due to water scarcity. This resulted in improved
farming practices that were immensely benefited by the
locals. The research was initiated by an experiment
conducted with only 16 green houses which later, due to
its enormous success, progressed to 200,000 farmers by
1994. With the increase in participation from the locals
within the province the rainwater harvesting projects
proved to be sustainable with 70% of the investments
coming from the locals themselves [6]. Since Malaysia is
a tropical country which is situated in a strategic location,
it receives rainfall throughout the year with no definite
significant dry period. The average rainfall of Malaysia is
greater than 2000mm which is more than enough for
developing a feasible system [7]. These facts would bring
one to the realization that rainwater harvesting should be
considered as a viable option for the consumption of
water within Malaysia but unfortunately that is not the
case. Rainwater harvesting awareness campaigns have
only begun after the shortage of water that the country has
faced owing to the water crisis in 1998. Due to the “El
Nino” phenomenon which has affected the region, the
level of water in three reservoir dams within Klang Valley
Preparation of Papers in Two-Column Format for International Journal of Chemical & Environmental Engineering
2
have dropped resulting in a large conservation and
rationing of water by the locals [8]. In this paper the
assessment of the rainwater harvesting within the
Multimedia University Campus, Malacca has been
studied. The objectives of this study are: to estimate the
potential of rooftop rainwater harvesting within the MMU
Melaka campus; to conduct a case study for irrigation of
football field in campus; and to determine the sizing of
the rainwater tank and its placement.
2. Methodology
2.1 Rainfall data
The rainfall data was acquired from a nearby
meteorological station which was in close vicinity to the
campus. Within the station there were two methods of
detecting rainfall, the traditional method by using a bottle
as a rain gauge and the more advanced AWS automatic
weather station’ method. The station only had available
data for four years’ worth of data (Jan 2008 – Dec 2011)
but which contained day to day precipitations along with
evaporation and humidity levels. Other rainfall data was
collected from the Tangki Nahrim program which was
developed by the National Hydraulic Research Institute of
Malaysia. Present within the program, are the average
monthly and annual precipitations starting from 1986 up
to 2006. Statistical formulas were also used in order to
obtain results regarding the daily capacity that could be
gathered. Table 1 shows average monthly rainfall from
1986 – 2006, Malacca Malaysia. While, Table 2 shows
the number of dry days (2008–2011) in Malacca,
Malaysia.
Table1: Average Monthly Rainfall from 1986 – 2006,
Malacca, Malaysia
Month Average Rainfall (mm)
Jan 34.3
Feb 70.3
Mar 142.4
Apr 179.2
May 180.4
Jun 177.1
Jul 217.4
Aug 202.9
Sep 189.6
Oct 196.1
Nov 225.3
Dec 150.3
Table 2: Number of Dry Days 2008 – 2011, Malacca,
Malaysia
Days Without Rainfall
2008 2009 2010 2011 Average Total
Jan 16 24 19 13 18 72
Feb 20 16 17 23 19 76
Mar 9 8 17 16 12.5 50
Apr 12 15 14 11 13 52
May 14 18 19 17 17 68
Jun 11 19 13 13 14 56
Jul 16 16 12 18 15.5 62
Aug 15 12 10 15 13 52
Sep 11 13 11 14 12.25 49
Oct 13 16 14 10 13.25 53
Nov 10 7 7 5 7.25 29
Dec 12 15 16 12 13.75 55
Total 159 179 169 167 168.5 674
2.2 Catchment area
As regards to the area of the rooftops, Google Earth was
utilized at first in order to calculate the rooftop area. The
image was subsequently compared with a template
obtained from Faculty and Management Division (FMD),
Multimedia University in order to identify the measure of
accuracy of the program. The result came to contain a
minor error with the original rooftop length being 68000
mm and the Google Earth result coming to a close 67.4 m
or 67400 mm. This resulted in an error of 0.88% which
was very low. Figure 1 shows Faculty of Engineering and
Technology (FET) rooftop area measurement, using
AutoCAD.
Figure 1: FET Rooftop Area Measurement, using
AutoCAD.
The amount of rainwater that is to be collected “V” can be
calculated by the catchment surface which used as given
in equation 1 [9],
Preparation of Papers in Two-Column Format for International Journal of Chemical & Environmental Engineering
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(1)
Where V is total rainwater collection (m
3), A is surface
area (m2), Y is precipitation (mm), and RC is runoff
coefficient. RC depends on the catchment surface. A is
the total area of the catchment surface and Y is the daily
rainfall. The three most common catchment surfaces are
tiles, corrugated metal sheets and concrete. Table 3 shows
type of roof surface along with run-off coefficient [10].
There were two types of rooftops within the MMU
Malacca Campus; the first was metal corrugated rooftops
while the other was concrete. The following table
describes the buildings with their corresponding rooftops.
Table 4 shows the buildings with rooftop material and
steepness.
Table 3: Type of Roof Surface along with Run-off
Coefficient [10]
No. Type of Roof Surface Run-off Coefficient
1 Tiles 0.8-0.9
2 Corrugated Metal Sheets 0.7-0.9
3 Concrete 0.6-0.8
2.3 Storage tank sizing
The sizing of the tank was selected based on the
necessities of water required by the football field within
the MMU Malacca campus. According to FMD, the
present field requires an irrigation amount of 1000 liters
per day, not including the natural replenishment received
from rainfall. This sizing is carried out by running a
simulation using MS Excel where economical and
meteorological factors are considered in the final
selection of the tank size. Also an important relation used
was the reliability factor which signifies the efficiency of
the rainwater harvesting system as a whole. It can be
defined as,
(2)
To calculate the tank capacity, an equation was
subsequently formulated based on the pattern of rainfall
and consumption of water by the football field.
Accordingly, constants were also placed within the
equation to keep the utilization of the tank as realistic as
possible. The equation is as follows,
(3)
Table 4: Buildings with Rooftop Material and Steepness
No. Buildings Rooftop Steepness
1 Block A (FBL) Concrete Flat
2 Block B Concrete Flat
3
Administration
Building
Metal
Sheets
Slight
Angle
4 FOSEE
Metal
Sheets
Slight
Angle
5 CITS 1 Concrete Flat
6 CITS 2 Concrete Flat
7 FET
Metal
Sheets
Slight
Angle
8 Main Hall & LP Concrete Flat
9 Plaza Siswa
Metal
Sheets
Slight
Angle
10 Law School
Metal
Sheets
Slight
Angle
11
Block T (Security
Office)
Metal
Sheets
Slight
Angle
12 FIST 1 Concrete Flat
13 FIST 2 Concrete Flat
14 Mosque Concrete Flat
15 CLC Lecture Complex
Metal
Sheets
Slight
Angle
16 CLC Auditorium 1 & 2
Metal
Sheets
Slight
Angle
17 CLC Auditorium 3 & 4
Metal
Sheets
Slight
Angle
18 Library
Metal
Sheets
Slight
Angle
Where x is previous day's capacity, A = 0 if tank's full,
B = 0 if tank <1, y is total rainfall received, z is daily
consumption and equal to 1m3, α is volume needed for
full capacity = tank size – x, θ = 90o when there is RF and
θ = 0o when there is no RF, and φ = 90
o when y<α and φ
= 0o if y>α.
2.4 Payback period
Payback period for harvesting rainwater system can be
calculated as:
(4)
The value of water saved can be defined as:
(5)
The total water saved can be express as:
Preparation of Papers in Two-Column Format for International Journal of Chemical & Environmental Engineering
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3. Results and Discussions
3.1 Rooftop area
The areas of the rooftops around campus were calculated
using AutoCAD program (Figure 1). The area was
calculated with relative ease by using the area function
present within the program. All the rooftops within the
campus are displayed along with its respective area
(Table 4). There are two types of buildings present within
the list, either concrete or metal. For future concerns, the
metal based rooftop could produce water that can be
suitable for drinking (after appropriate treatment) as well
as other domestic applications, whereas the concrete
based rooftops are only suitable for irrigation purposes.
With the help of these roof catchment areas, an overall
potential of rainwater collection volume can be calculated
with the help of the average monthly rainfall (Table 1)
multiplying with a runoff coefficient of 0.8 due to
concrete and metal rooftops, we get a potential of 2720.7
m3.
3.2 Humidity and evaporation
From the daily meteorological data (Table 5), it is
apparent that the evaporation rate is highly affected by the
temperature, humidity and daily total solar radiation. The
lower the humidity level, the higher the evaporation rate
because of the tiny amount of water present within the air.
This fact shows that more irrigation is required with days
with less humidity levels due to the increase in
evaporation.
3.3 Elevation and tank placement
By reviewing the campus in a more geographical
perspective, it is quite clear that there is considerable
variation between the elevations of the buildings with
respect to the football field. The MMU Malacca campus
is constructed along Bukit Beruang which is a hill situated
adjacent to the campus. In the Figure 2, the difference in
elevation is calculated by the use of Google Earth for the
FOSEE building and the football field within campus.
The highest and lowest points come at the ends of the
white line that can be seen within the Figure 2. The first
end coming out at 22m was located at the football field
while the other end was at 36m. The latter point wasn’t
placed at the roof of the FOSEE building but to the
adjacent parking lot at ground level. The difference
between the elevations came out to be 14m. FOSEE was
chosen as a subject of study because of its considerable
roof capacity and its favorable location, which was the
highest when compared to other buildings within campus.
Due to these factors, suitable and ease of delivering the
water to the field by gravity, eliminating the use of pump.
The placement of the tank was chosen at the parking lot
next to the building serving adequate space and height for
water delivery to the field as can be seen in Figure 2.
Table 5: Humidity and Evaporation Rate, Jan 2009,
Malacca
Day Humidity % Evaporation [mg/(m2.s)]
1 87 2
2 66 5
3 89 1.1
4 59 3.5
5 49 4.6
6 49 6
7 55 5.8
8 52 5.4
9 56 7
10 60 3
11 59 5.2
12 53 5.8
13 60 7.4
14 54 7.1
15 53 7.3
16 49 7.9
Figure 2: Elevation between FOSEE and Football Field
and Tank Placement, Google Earth
Preparation of Papers in Two-Column Format for International Journal of Chemical & Environmental Engineering
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3.4 Pipeline
Figure 3 shows the route from the tank to the football
field. The route utilizes the rain water drain system within
campus therefore no excavation of any kind is required.
With an elevation of 14 m enough water flow can be
achieved in order to irrigate the field. This could
minimize the expenditure on pumps and the eventual
consumption of electricity for the system. With the help
of the elevated terrain the field could be irrigated with the
help of gravity alone.
Table 6 shows the piping details for the route from
the tank to the football field. The dimensions were
calculated using a pipe flow calculator known as the Pipe
Flow Wizard. This program helps in calculating desired
flow, pressure, diameter and length of a piping system. It
was user friendly where certain values of the system had
to be entered initially to obtain the desired parameter. A
standard inner diameter of 52 mm ‘Rigid PVC Pipe’ was
selected in order to obtain a flow of at least 11 m3/hr
(standard domestic flow rate). Also the length of the route
was entered as 284 m. The elevation from the inlet to the
exit was 14 m as mentioned earlier (elevation between
FOSEE and the football field). The eventual flow rate that
was calculated came out to be 16.488 m3/hr with a fluid
velocity of 2.157 m/s. This was found satisfactory in
terms of irrigation therefore eliminating the use of a
pump.
Figure 3: Pipe Route from Tank to Football Field
3.5 Rainwater tank sizing With the help of Excel a realistic approach was taken in
regards to the effectiveness of the rainwater harvesting
system and the amount of days the tank would in fact
irrigate the football field. Also, a much more detailed
analysis was conducted as to how much water would
actually be saved. The year 2009 (Table 2) was taken as a
sample to conduct the analysis out of the other three years
due to its elongated dry days which can be seen from
Table 2 as 179 days, which is 49% of the entire year. The
flow chart for the simulation of the tank is shown in
Figure 4.
Table 6: Piping Details, Tank to Football Field
Pipe material Rigid PVC
Internal diameter 52 mm
Internal roughness 0.005 mm
Length 283 m
Pipe fittings 12
Standard 90o bend 8
Elbow 45° 3
Gate valve (100%) 1
Total 'K' value of
fittings 5.33
Elevation change 14 m Fall
Flow 16.488 m³/hr
Fluid Water @ 20°C (68°F)
Flow type Turbulent
Reynold's number 111699
Friction factor 0.018
Fluid velocity 2.157 m/s
Figure 4: Flow Chart for Simulation of Tank
With the help of the equation 3, the tank’s behavior was
computer-generated using MS Excel. The most obvious
solution was to choose a tank with the highest reliability
rate. But that may deem financially unsuitable. Therefore,
lists of tanks sizes along with their prices were compared
Preparation of Papers in Two-Column Format for International Journal of Chemical & Environmental Engineering
6
to the amount of water that was being saved. This helped
calculating the payback period of the tank. Table 7 shows
the tank sizes with reliability and payback period.
From Table 7 it can be observed that the cost of the tanks
increases with size. This however was not the same when
the payback period was concerned. It could be seen that
the fastest return was delivered by the 5 m3 tank. This was
due to high reliability rate and increased water savings but
lower costs. The maximum reliability is held by the 10 m3
tank however it gives the second worst payback period. It
should be noted that although the 10 m3 tank is quite
capable, the savings that were produced were only RM
36.4 more annually than the 5 m3 tank. By looking at the
high number of dry days within the year which is the most
out of the other three, it would be easy to assume that the
10 m3 tank would irrigate much more days due to its
much larger volume. But on the contrary, it only exceeded
in irrigating by a mere 28 days than its counterpart which
is twice its size. This proves that lower sized tanks,
although cheaper cannot pay back their investment quick
enough and higher sized tanks, although larger in capacity
do not irrigate at a much higher rate. Therefore the right
size of the tank should serve the purpose of irrigation well
enough and also payback its investment at the quickest
time.
Table 7: Tank Sizes with Reliability and Payback Period
Tank
Size
(m3) Reliability Savings
Tank
Cost
P.B
Period
(years)
1.5 32%
RM
83.20
RM
2,035.20 24.46
2.55 52%
RM
137.80
RM
2,210.10 16.04
3.275 65%
RM
170.30
RM
2,639.40 15.50
4.2 71%
RM
185.90
RM
2,957.40 15.91
5 78%
RM
205.40
RM
2,893.80 14.09
10 92%
RM
241.80
RM
4,801.80 19.86
4. Conclusions
The assessment of the rainwater harvesting within the
Multimedia University Campus, Malacca has been
studied. The case study is carried out based on the
football field within campus. The field consumes 1 m3 of
water every non-rainy day. According to the results, the
catchment size for the FOSEE building which comes to
about 1214 m2 was adequate for collection of rainwater.
The sizing of the tank at 5 m3 is most beneficial in terms
of pay-back and reliability.
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